CN104956998B - A kind of biodegradable afforestation device and method of forestation - Google Patents
A kind of biodegradable afforestation device and method of forestation Download PDFInfo
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- CN104956998B CN104956998B CN201510347318.1A CN201510347318A CN104956998B CN 104956998 B CN104956998 B CN 104956998B CN 201510347318 A CN201510347318 A CN 201510347318A CN 104956998 B CN104956998 B CN 104956998B
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- seedling
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- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G17/00—Cultivation of hops, vines, fruit trees, or like trees
- A01G17/04—Supports for hops, vines, or trees
- A01G17/14—Props; Stays
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G13/00—Protecting plants
- A01G13/02—Protective coverings for plants; Coverings for the ground; Devices for laying-out or removing coverings
- A01G13/0206—Canopies, i.e. devices providing a roof above the plants
- A01G13/0212—Canopies, i.e. devices providing a roof above the plants for individual plants, e.g. for plants in pots
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01G—HORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
- A01G13/00—Protecting plants
- A01G13/02—Protective coverings for plants; Coverings for the ground; Devices for laying-out or removing coverings
- A01G2013/0218—Protective coverings for plants; Coverings for the ground; Devices for laying-out or removing coverings for removing
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Botany (AREA)
- Environmental Sciences (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Toxicology (AREA)
- Biological Depolymerization Polymers (AREA)
- Cultivation Of Plants (AREA)
Abstract
The invention provides a kind of biodegradable afforestation device and method of forestation; biodegradation afforestation device includes seedling diaphragm and the pillar to support diaphragm; the pillar is distributed in the seedling surrounding centered on seedling, and the seedling diaphragm is enclosed on the pillar periphery.Seedling is protected using the afforestation device comprising white biodegradable plastic cylinder film and bamboo stick or waddy; a metastable microhabitat is provided for seedling early stage existence, development is grown into seedling, protection device is slowly degraded; manual demolition process is eliminated, cost of forestation has been saved.Seedling base portion lays organic mat in protection device, not only reduces soil water evaporation, it is suppressed that weed growth, and improves soil texture, promotes growing for seedling later stage.
Description
Technical field
The invention belongs to Forest Cultivation technical field, and in particular to a kind of biodegradable afforestation device and method of forestation.
Background technology
Difficult site refers to the difficult site type of afforestation, these regional often droughts, is air-dried, lacks plant
Quilt, Evapotranspiration of The Soil Water is strong, and seedling dehydration is serious when causing afforestation, and rhizome is prone to evil of burning day, ground, underground position
Physiological coordination multilated, directly weaken afforestation seedling survival ability, therefore Difficult site be always ecological construction and
The crucial target area of restoration of the ecosystem.It is existing that the selection of Difficult site preferent, habitat improving technology, technology for recovering vegetation etc. are studied
It is more, also form a series of afforestation key technologies for different Difficult site types.Persistently carry out new afforestation technology to grind
Study carefully, simplify afforestation process, reduce difficulty of construction, the seedling surrival rate of afforestation is improved conscientiously, to solving Difficult site problem meaning weight
Greatly.
The content of the invention
In view of this, the invention reside in a kind of biodegradable afforestation device and method of forestation is provided, solve in Difficult site
The crucial problem such as cause seedling percent low, slow-growing because the fine heated drying of weather, Evapotranspiration of The Soil Water are strong etc. during afforestation.
The present invention is achieved through the following technical solutions：
A kind of biodegradable afforestation device, it is characterised in that the pillar including seedling diaphragm and to support diaphragm,
The pillar is distributed in the seedling surrounding centered on seedling, and the seedling diaphragm is enclosed on the pillar periphery.
Above-mentioned biodegradable afforestation device, the seedling diaphragm is the white biodegradable plastic cylinder film communicated up and down；
The pillar is bamboo stick or waddy.
The difference of above-mentioned biodegradable afforestation device, the strut lengths and the seedling diaphragm height is more than or waited
In 20 centimetres.
Above-mentioned biodegradable afforestation device, the pillar is three, and is evenly distributed on centered on seedling the children
Seedling surrounding.
A kind of biodegradable method of forestation, comprises the following steps：
(1) seedling is transplanted；
(2) select around seedling at 2 points, respectively insert the first pillar and the second pillar in soil；
(3) seedling diaphragm is enclosed on first pillar and second pillar；
(4) seedling diaphragm is strutted with the 3rd pillar, and set surrounds seedling；
(5) adjustment orientation makes first pillar, second pillar and the 3rd pillar are distributed in triangular shape, and makes
The seedling diaphragm is unfolded and tightened, and then the 3rd pillar is inserted perpendicularly into soil.
Above-mentioned biodegradable method of forestation, also comprises the following steps (6) after step (5)：Organic mat is uniform
It is sprinkling upon in the seedling diaphragm for surrounding triangular shape, and covers seedling base portion, organic mat thickness is 3-5cm.
Above-mentioned biodegradable method of forestation, in step (6)：The organic mat includes the loose squama layer that becomes thoroughly decomposed.
Above-mentioned biodegradable method of forestation, the preparation method for the loose squama that becomes thoroughly decomposed is as follows：Pine bark is collected, pine bark is crushed to
Particle diameter is 0.1-1mm, and bacillus subtilis stoste is added into obtained pine bark powder and is mixed thoroughly, in bacillus subtilis stoste
Viable bacteria total concentration is 1 × 106~1012CFU/mL, the addition of bacillus subtilis stoste is grabbed pine bark powder with hand and just oozed out
Water is defined, heap corruption 30~40 days, during which stirred and is mixed thoroughly once every 5 days.
Above-mentioned biodegradable method of forestation, in step (6)：Organic mat also includes being sequentially located at the loose squama that becomes thoroughly decomposed
Deer natural pond soil layer and the stalk layer that becomes thoroughly decomposed below layer, deer natural pond the thickness of the layer is 0.5~1.5 centimetre, the stalk layer that becomes thoroughly decomposed
Thickness be 1-2 centimetres；The preparation method of the stalk layer that becomes thoroughly decomposed is as follows：Take powder of straw, or powder of straw and peanut shell powder is mixed
Compound, or powder of straw, peanut shell powder and corn flour mixture；Add viable bacteria total concentration in lactic acid bacteria stoste, lactic acid bacteria stoste
For 1 × 108~1012CFU/mL；The addition of lactic acid bacteria stoste grabs mixture by hand, and just water seepage is defined, heap corruption 70~80
My god.
Above-mentioned biodegradable method of forestation, the seedling diaphragm is the white biodegradable plastic cylinder film communicated up and down；
First pillar, second pillar and the 3rd pillar are bamboo stick or waddy, and are uniformly divided centered on seedling
Cloth is in the seedling surrounding.
The beneficial effects of the invention are as follows：Biodegradable afforestation device of the invention is reasonable in design, easy to operate, raw comprising white
The protection device of thing degradative plastics cylinder film and bamboo stick or waddy, a metastable micro- life is provided for seedling early stage existence
Border, development is grown into seedling, and protection device is slowly degraded, eliminates manual demolition process, saved cost of forestation, seedling
Survival rate is greatly improved.Seedling base portion lays organic mat in protection device, not only reduces soil water evaporation, suppresses
Weed growth, and soil texture is improved, promote growing for seedling later stage.
Brief description of the drawings
The structural representation of the biodegradable afforestation device of Fig. 1 present invention.
The top view of the biodegradable afforestation device of Fig. 2 present invention.
In figure：1- seedling diaphragms；2- pillars；The pillars of 21- first；The pillars of 22- second；The pillars of 23- the 3rd；3- seedling.
Embodiment
For the scheme in the clear explanation present invention, preferred embodiment is given below and is described with reference to the accompanying drawings.
Embodiment 1
As depicted in figs. 1 and 2, a kind of biodegradable afforestation device, including seedling diaphragm 1 and to support diaphragm
Pillar 2, the pillar 2 is distributed in the seedling surrounding centered on seedling, and the seedling diaphragm 1 is enclosed on outside the pillar 2
Enclose.In the present embodiment, the seedling diaphragm 1 is the white biodegradable plastic cylinder film communicated up and down；The pillar 2 is bamboo stick
Or waddy.The difference of the length of pillar 2 and the height of seedling diaphragm 1 is equal to 20 centimetres.Propped up described in the present embodiment
Post 2 is three, and is evenly distributed on centered on seedling the seedling surrounding.The present embodiment it is reasonable in design, it is easy to operate,
Comprising white biodegradable plastic cylinder film and bamboo stick or waddy protection device, for seedling early stage existence provide one it is relatively steady
Fixed microhabitat, development is grown into seedling, and protection device is slowly degraded, eliminates manual demolition process, saved afforestation
Cost.
Embodiment 2
A kind of biodegradable method of forestation, using the biodegradable afforestation device in embodiment 1, comprises the following steps：
(1) seedling is transplanted；
(2) select around seedling at 2 points, the first pillar 21 and the second pillar 22 are inserted into 10-20 centimetres of soil respectively；
(3) seedling diaphragm 1 is enclosed on first pillar 21 and second pillar 22；
(4) seedling diaphragm 1 is strutted with the 3rd pillar 23, and set surrounds seedling；
(5) adjustment orientation makes first pillar 21, second pillar 22 and the 3rd pillar 23 in triangular shape point
Cloth, and the seedling diaphragm 1 is unfolded and is tightened, the 3rd pillar 23 is then inserted perpendicularly into 10-20 centimetres of soil；Institute
It is the white biodegradable plastic cylinder film (diameter 50cm, high 50cm) communicated up and down to state seedling diaphragm 1；First pillar
21st, second pillar 22 and the 3rd pillar 23 are bamboo stick or waddy, and are evenly distributed on centered on seedling described
Seedling surrounding；
(6) organic mat is uniformly sprinkling upon in the seedling diaphragm for surrounding triangular shape, and covers seedling base portion, this reality
Organic mat described in example is applied for the commercially available loose squama that becomes thoroughly decomposed, the loose squama thickness degree that becomes thoroughly decomposed is 3cm, the loose squama that becomes thoroughly decomposed can play water conservation,
Weed seed is free of in the effect of fertilizer conservation, and the loose squama that becomes thoroughly decomposed, it is to avoid seedling base portion is weedy.
Spring in 2012, tested using the biodegradable method of forestation of the present embodiment, test site is Zhejiang Province's Anji County
Mine tailing area, experiment is respectively bitter sweet oak, Zhejiang persimmon and soapberry with seeds, transplants 200 plants of seedling respectively, bitter sweet oak, Zhejiang persimmon and
The survival rate of soapberry is followed successively by 80.0%, 84.0%, 92.5%；Without using the method for the present embodiment, and use common plantation
Method of forestation, the survival rate of bitter sweet oak, Zhejiang persimmon and soapberry is followed successively by 55.0%, 62.5%, 70.5%.Autumn in 2013, in vain
Color Plastic barrel film is gradually degraded, and growth of seedling is good.
Embodiment 3
The present embodiment is the parallel check experiment of embodiment 2, and the difference of itself and embodiment 2 is：The loose squama that becomes thoroughly decomposed is voluntarily
Production, the preparation method for the loose squama that becomes thoroughly decomposed is as follows：Pine bark is collected, pine bark particle diameter is crushed to for 0.5-1mm, to what is obtained
Bacillus subtilis stoste is added in pine bark powder and is mixed thoroughly, viable bacteria total concentration is 1 × 10 in bacillus subtilis stoste12CFU/
ML, the addition of bacillus subtilis stoste grabs pine bark powder by hand, and just water seepage is defined, and heap is rotten 40 days, during which every 5 days
Stir and mix thoroughly once.The loose squama that becomes thoroughly decomposed voluntarily produced in this implementation can not only play a part of water conservation, fertilizer conservation, and can keep away
Exempt from seedling base portion caused by severe natural conditions cause injury it is pathogenic, while pest and disease damage can be prevented and treated.
Spring in 2012, tested using the biodegradable method of forestation of the present embodiment, test site is Zhejiang Province's Anji County
Mine tailing area, experiment is respectively bitter sweet oak, Zhejiang persimmon and soapberry with seeds, transplants 200 plants of seedling respectively, bitter sweet oak, Zhejiang persimmon and
The survival rate of soapberry is followed successively by 82.5%, 87.0%, 94.0%.Autumn in 2013, white plastic cylinder film is gradually degraded, seedling life
It is long good.
Embodiment 4
The present embodiment is the parallel check experiment of embodiment 3, and the difference of itself and embodiment 3 is：Organic mat is also wrapped
The deer natural pond soil layer being sequentially located at below the loose squama layer that becomes thoroughly decomposed and the stalk layer that becomes thoroughly decomposed are included, deer natural pond the thickness of the layer is 0.5 li
Rice, the thickness of the stalk layer that becomes thoroughly decomposed is 1 centimetre；The preparation method of the stalk layer that becomes thoroughly decomposed is as follows：Take the straw for being crushed to 300 mesh
Stalk powder, it is 1 × 10 to add viable bacteria total concentration in lactic acid bacteria stoste, lactic acid bacteria stoste8CFU/mL；The addition of lactic acid bacteria stoste with
Hand grabs mixture, and just water seepage is defined, and heap is rotten 70 days.
Spring in 2012, tested using the biodegradable method of forestation of the present embodiment, test site is Zhejiang Province's Anji County
Mine tailing area, experiment is respectively bitter sweet oak, Zhejiang persimmon and soapberry with seeds, transplants 200 plants of seedling respectively, bitter sweet oak, Zhejiang persimmon and
The survival rate of soapberry is followed successively by 88.0%, 88.5%, 95.0%.Autumn in 2013, white plastic cylinder film is gradually degraded, seedling life
It is long good.
Embodiment 5
The present embodiment is the parallel check experiment of embodiment 3, and the difference of itself and embodiment 3 is：Organic mat is also wrapped
The deer natural pond soil layer being sequentially located at below the loose squama layer that becomes thoroughly decomposed and the stalk layer that becomes thoroughly decomposed are included, deer natural pond the thickness of the layer is 0.5 li
Rice, the thickness of the stalk layer that becomes thoroughly decomposed is 1 centimetre；The preparation method of the stalk layer that becomes thoroughly decomposed is as follows：Take and be crushed to 300 mesh respectively
Powder of straw and peanut shell powder, the mass ratio of powder of straw and peanut shell powder is 1:2, mix mixing thoroughly；Add lactic acid bacteria stoste, lactic acid
Viable bacteria total concentration is 1~10 in bacterium stoste12CFU/mL；The addition of lactic acid bacteria stoste using hand grab mixture just water seepage as
Standard, heap is rotten 80 days.
Spring in 2012, tested using the biodegradable method of forestation of the present embodiment, test site is Zhejiang Province's Anji County
Mine tailing area, experiment is respectively bitter sweet oak, Zhejiang persimmon and soapberry with seeds, transplants 200 plants of seedling respectively, bitter sweet oak, Zhejiang persimmon and
The survival rate of soapberry is followed successively by 92.5%, 90.0%, 96.5%.Autumn in 2013, white plastic cylinder film is gradually degraded, seedling life
It is long good.
Embodiment 6
The present embodiment is the parallel check experiment of embodiment 3, and the difference of itself and embodiment 3 is：Organic mat is also wrapped
The deer natural pond soil layer being sequentially located at below the loose squama layer that becomes thoroughly decomposed and the stalk layer that becomes thoroughly decomposed are included, deer natural pond the thickness of the layer is 0.5 li
Rice, the thickness of the stalk layer that becomes thoroughly decomposed is 1 centimetre；The preparation method of the stalk layer that becomes thoroughly decomposed is as follows：Take and be crushed to 300 mesh respectively
Powder of straw, peanut shell powder and corn flour, the mass ratio of powder of straw, peanut shell powder and corn flour three is 1:2:0.1, mixing is mixed
It is even；It is 1 × 10 to add viable bacteria total concentration in lactic acid bacteria stoste, lactic acid bacteria stoste10CFU/mL；The addition of lactic acid bacteria stoste is with hand
Grabbing mixture, just water seepage is defined, and heap is rotten 75 days.
Spring in 2012, tested using the biodegradable method of forestation of the present embodiment, test site is Zhejiang Province's Anji County
Mine tailing area, experiment is respectively bitter sweet oak, Zhejiang persimmon and soapberry with seeds, transplants 200 plants of seedling respectively, bitter sweet oak, Zhejiang persimmon and
The survival rate of soapberry is followed successively by 98.5%, 91.0%, 99.0%.Autumn in 2013, white plastic cylinder film is gradually degraded, seedling life
It is long good.
Above-described embodiment is only intended to clearly illustrate the invention example, and not has to the invention
The restriction of body embodiment.For those of ordinary skill in the field, it can also make on the basis of the above description
Other various forms of changes or variation.There is no necessity and possibility to exhaust all the enbodiments.It is all the present invention
Guarantor of any obvious changes or variations extended out within spirit and principle still in the invention claim
Protect among scope.
Claims (1)
1. a kind of biodegradable method of forestation, it is characterised in that comprise the following steps：
(1) seedling is transplanted, and seedling is bitter sweet oak, Zhejiang persimmon and soapberry；
(2) select around seedling at 2 points, the first pillar (21) and the second pillar (22) are inserted into 10-20 centimetres of soil respectively；
(3) seedling diaphragm (1) is enclosed on first pillar (21) and second pillar (22)；
(4) seedling diaphragm (1) is strutted with the 3rd pillar (23), and set surrounds seedling；
(5) adjustment orientation makes first pillar (21), second pillar (22) and the 3rd pillar (23) be in triangular shape
Distribution, and the seedling diaphragm (1) is unfolded and is tightened, the 3rd pillar (23) is then inserted perpendicularly into soil 10-20
Centimetre；The seedling diaphragm (1) is the white biodegradable plastic cylinder film communicated up and down, the white biodegradable plastic cylinder
Film diameter 50cm, high 50cm；First pillar (21), second pillar (22) and the 3rd pillar (23) be bamboo stick or
Waddy, and it is evenly distributed on centered on seedling the seedling surrounding；
(6) organic mat is uniformly sprinkling upon in the seedling diaphragm for surrounding triangular shape, and covers seedling base portion, it is described organic
Covering includes becoming thoroughly decomposed loose squama layer and the deer natural pond soil layer and the stalk layer that becomes thoroughly decomposed that are sequentially located at below the loose squama layer that becomes thoroughly decomposed；
The loose squama thickness degree that becomes thoroughly decomposed is 3cm, and the preparation method for the loose squama that becomes thoroughly decomposed is as follows：Pine bark is collected, pine bark is crushed to particle diameter
For 0.5-1mm, bacillus subtilis stoste is added into obtained pine bark powder and is mixed thoroughly, viable bacteria in bacillus subtilis stoste
Total concentration is 1 × 1012CFU/mL, the addition of bacillus subtilis stoste grabs pine bark powder by hand, and just water seepage is defined, heap
It is rotten 40 days, during which stirred and mixed thoroughly once every 5 days；
Deer natural pond the thickness of the layer is 0.5 centimetre, and the thickness of the stalk layer that becomes thoroughly decomposed is 1 centimetre；
The preparation method of the stalk layer that becomes thoroughly decomposed is as follows：The powder of straw for being crushed to 300 mesh respectively, peanut shell powder and corn flour are taken,
The mass ratio of powder of straw, peanut shell powder and corn flour three is 1:2:0.1, mixing is mixed thoroughly；Lactic acid bacteria stoste is added, lactic acid bacteria is former
Viable bacteria total concentration is 1 × 10 in liquid10CFU/mL；The addition of lactic acid bacteria stoste grabs mixture by hand, and just water seepage is defined, heap
It is rotten 75 days.
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| CN201510347318.1A CN104956998B (en) | 2015-06-19 | 2015-06-19 | A kind of biodegradable afforestation device and method of forestation |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106688768A (en) * | 2016-11-17 | 2017-05-24 | 南京林业大学 | Covering method capable of improving organic matter in sweet-scented osmanthus soil and promoting Osmanthus fragrans Cv rixianggui to grow |
| CN107135859A (en) * | 2017-04-18 | 2017-09-08 | 天津农学院 | A kind of method that use degradable device protects robur seedling |
| CN109496495B (en) * | 2018-12-28 | 2021-07-20 | 河北省林业和草原科学研究院 | Quercus seed breeding device and planting method |
Family Cites Families (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1987004897A1 (en) * | 1986-02-15 | 1987-08-27 | David George Holladay | Improvements relating to plant shelters |
| FI921628A (en) * | 1992-04-10 | 1993-10-11 | Agrame Ab Oy | APPARAT FOER PLANTSKYDD |
| JP3982942B2 (en) * | 1999-04-22 | 2007-09-26 | アキレス株式会社 | Seedling protective cover |
| US7669364B2 (en) * | 2004-11-30 | 2010-03-02 | Miami University | Devices, kits, and methods for providing protection to plants |
| JP3842809B2 (en) * | 2005-08-19 | 2006-11-08 | ハイトカルチャ株式会社 | Overflow area greening method |
| US8215055B2 (en) * | 2009-06-11 | 2012-07-10 | Miller Cameron M | Protective guard for use with vegetation |
| CN103026935A (en) * | 2012-12-26 | 2013-04-10 | 华南师范大学 | Mangrove plant big seedling transplantation protective cover and application thereof |
| CN203194226U (en) * | 2013-04-11 | 2013-09-18 | 湖北省烟草公司襄阳市公司 | Tobacco seedling protective device |
| CN104692961A (en) * | 2015-02-03 | 2015-06-10 | 新疆天物生态科技股份有限公司 | Microorganism organic material decomposition agent as well as preparation method and applications thereof |
-
2015
- 2015-06-19 CN CN201510347318.1A patent/CN104956998B/en active Active
Non-Patent Citations (3)
| Title |
|---|
| 半高丛蓝莓品种北陆限根栽培关键技术;董畅等;《中国果树》;20141130(第6期);第60-61页 * |
| 蓝莓栽培技术;周鹤;《河北果树》;20140731(第4期);第53-54页 * |
| 蓝莓栽培技术;许艳玲等;《现代农业科技》;20110531(第9期);第122页 * |
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